Team:Minnesota/Templates
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Revision as of 17:37, 17 October 2014
Minnesota iGEM 2014
Project
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To design a system for biological remediation of not only mercury ions in contaminated waters, but also the more toxic form, methyl mercury, we’ve selected to use 5 genes of the mercury resistance (mer) operon of which over 10 genes have been identified and characterized in various strains of mercury resistant bacteria in the environment. This construct was assembled from the mer operon in Serratia marscecens in the plasmid pDU1358, and is designed to contain an upstream regulatory gene merR, two transport proteins merP (periplasmic) and merT (transmembrane), a gene encoding mercuric reductase MerA, and finally a gene encoding organomercurial lyase MerB. This system is regulated by a bidirectional promoter so that merR on one side of the operon is constitutively expressed and allows for the repression of the mer operon in the absence of mercury ions, and the downstream activation and transcription of merT, P, A, B when mercury ions are in close proximity.
MerT and MerP were selected as transporters for their high turnover rates to bring in mercury ions, which are subsequently bound by MerA to catalyze their conversion into volatile mercury eventually captured within a carbon filter in our device and disposed of sustainably. The organic and more toxic form, methylmercury, can diffuse into the cytosol of the bacteria where MerB catalyzes its conversion into mercury ions, which are then bound to MerA and converted into less toxic, volatile elemental mercury in an NADP dependent reaction. The system is very tightly regulated and allows for continuous turnover within our bacterial chassis as the mercury ions are volatalized and then captured externally rather than sequestered within our bacteria which would eventually lead to cell death and the requirement to replace the cells. Due to the NADP requirement of MerA, the cells are required to stay alive throughout this process, accounted for this with novel cell encapsulation technology that allows the cells to remain viable and at the same time not in direct contact..?
Our system was tested in 3 different chassis: E. coli, Pseudomonas, and Shewanella, encapsulated and unencapsulated in the presence of either mercury chloride or methylmercury chloride and showed very promising results!
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Fig 1 illustrating the relative positions of Mer proteins within the cell, modified mer operon.
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Biobrick Assembly
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The phsABC genes from Salmonella enterica serovar Typhimurium LT2 encode thiosulfate reductase, which catalyzes the stoichiometric production of hydrogen sulfide and sulfite from thiosulfate for heavy metal removal by precipitation. Within a separate bacterium from that containing the mer operon construct, This system allows us to extend our heavy metal bioremediation device to be applicable to a wide range of heavy metals in addition to mercury in both ionic and organic form. The phsABC operon encodes three open reading frames (ORFs), designated phsA, phsB, and phsC. Based on sequence homology to formate dehydrogenase-N, it is predicted that thiosulfate reductase behaves in a similar fashion. The PhsA subunit is predicted to be a peripheral membrane protein active site bis(molybdopterin guanine dinucleotide) molybdenum (MGD) cofactor. PhsC is an integral membrane protein that anchors the other two subunits to the membrane, and contains the site for menaquinol oxidation and two heme cofactors located at opposite sides of the membrane. PhsB is predicted to possess four iron-sulfur centers that transfer electrons between PhsC and PhsA. was shown to have the highest catalytic activity in the IPTG- inducible plasmid pSB74. The part was used by the Yale 2010 iGEM Team (Part:BBa_K393000) (inducible by IPTG) to deposit copper sulfide in a specified geometry. We sought to both improve and characterize this part for future utilization in our filtration device by adding a modified lac promoter to allow for constitutive expression rather than IPTG induction within the biological system, and thus make it more applicable in the environment (Figure 5). We also improved the characterization of their part by testing its application for biological precipitation of iron and cadmium in addition to their copper testing to add to the functionality of the part. |
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Biobrick Assembly
Modified construct containing “phsABC”. The phsABC operon was amplified from the pSB74 plasmid and inserted into pSB1C3 (shipping vector) and the pBBRBB plasmid (for characterization) with the novel addition of a constitutive promoter.
Biosafety
In response to our survey results showing that there was some concern about the bacteria escaping the device, we have designed two kill switches to address this concern and highlighted their advantages and disadvantages. Click either of the pictures below to view more information on each proposal.
Kill Switch 1 |
Kill Switch 2 |
Fig Zones of Inhibition Test For Mercury Resistance. |
In this assay, Escherichia coli K12 expressing three different constructs were spread on agar plates to compare levels of mercury resistance. Each agar plate contained a filter disk spotted with 10µL of 0.1M HgCl2 in the middle. ++++++ |
Fig Zones of Inhibition Test For Mercury Resistance. |
Zones of Inhibition Test For Mercury Resistance. In this assay, Escherichia coli K12 expressing three different constructs was spread on agar plates to compare levels of mercury resistance. Each agar plate contained a filter disk spotted with 10µL of 0.1M HgCl2 in the middle. (A) Agar Plates of K12 with each construct. Left, K12 containing pBBRBB::mer (mer operon); center, K12 containing pBBRBB::gfp (vector control); right, K12 containing pBBRBB::merΔmerA(mer operon with merA deleted). (B) Diameter of zones of inhibition. The diameter of the zone of inhibition was measured in triplicate. Green corresponds to pBBRBB::gfp, blue to pBBRBB::merRTPAB, and red to pBBRBB::merΔmerA. Individual constructs range from highest resistance in the following order: merRTPAB > vector control >merΔmerA. Our results show that both the recombinant E. coli and Pseudomonas putida containing the pBBRBB::mer plasmid were able to grow significantly closer to the HgCl2 disc than the negative control (pBBRBB::GFP). The E.coli strain containing the merA deletion plasmid could not survive as close to the heavy metal spotted disc as the negative control. This is likely due to the fact that it still contains the transport proteins MerP and MerT, and therefore transports the toxic mercury ions into the cell without remediating it due to the lack of MerA, causing cell death. On the other hand, the pBBRBB::GFP control was not able to take up any mercury ions. |
MethyllMercury Results
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The main goal of EncapsuLab was to create a system for the preservation and protection of the bacteria in our system,
as well as physically separating them from the outside environment. To achieve this, we created a water-porous
silica matrix using techniques developed by the Aksan and Wackett labs at the U of M. Furthermore, we developed
a device to work as a proof of concept for the use of encapsulated bacteria in a real water-cleaning system.
In addition to this, we conceptualized a scaling-up of our system for larger water-cleaning problems. Lastly,
we developed a mathematical model to compare our experimental data in order to better understand the biochemical networks behind our work.
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Encapsulation Procedure
To make a silica matrix surrounding a cell, we needed a supply of silica nanoparticles and a reactive cross-linker capable of
covalently bonding reagents into a unified volume. Two solutions were prepared: one was a combination of TM-40 (colloidal
silica) and diluting components (ultrapure water and polyethylene glycol). The second solution was tetramethyl orthosilicate
(TMOS) cross-linker. In slightly acidic conditions, methyl groups of TMOS are hydrolyzed, producing methanol and the silica
cross-linker. Resuspended and washed cells are then added to the relatively innocuous colloidal solution. Upon combining
these two mixtures, a rapid polymerization linking colloidal silica together occured. In order to achieve proper bead
sphericity, we combined all of these components in an hydrophobic solution and let them set. After some experimentation, we
were able to produce beads with a consistent size. To purify the mixture, we phase-separated the silica beads by adding
water to solution, which forced them into the aqueous phase. These were then recovered to assess viability.
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Mathematical Modeling
The equations used in conversion steps 3 and 4 are extracted from studies done by Maria on ionic mercury uptake by E. coli
cells (Maria, 2010). These equations can be used because ionic mercury is converted into elemental mercury which in turn
diffuses into the extracellular space; these two steps were described in the Maria paper. It is assumed that methylmercury
and ionic mercury have similar orders of magnitude of transport rate into the cell.
Since step 2 is not explicitly included in the Maria paper, a different approach was used to determine the equation. During
our literature search, we did not find any primary publications that specify the methylmercury conversion behavior of both
MerA and MerB. Our pBBRBB plasmid is designed in the way that the mer genes are induced in the presence of methylmercury and
ionic mercury. Through our literature search, we were able to calculate the steady state concentrations of basal and induced
states based on the presence of methlymercury and ionic mercury in the cytosolic space. Therefore, we used the below
equation to extrapolate the reaction rates of both the mer proteins. For details, please see Supplemental Materials A.
The above equations show the reaction rates of the mer proteins under induced steady state. To represent the full MerA and
MerB expression, we include terms for the basal protein expression, the induction of the Mer proteins, and the degradation
of proteins. For details on the calculations, please refer to Supplemental Materials A. We have determined from our
calculations that Va and Vb resemble Vmax in the equations.
Sensitivity Analysis
We performed sensitivity analysis to give us insight into which parameters will have the greatest effect on each species in
the reaction equations. We calculated the local derivatives of each species with respect to the parameters to determine how
much the parameters affected the result. The concentration of methylmercury in the cytoplasm was found to be most sensitive
to the V and K parameters of MerB. Additionally, the concentration of Hg in the extracellular space and cytosol were both
most sensitive to the V and K parameters of MerA. We can use this sensitivity analysis as a guide to what parameters are most
useful to improve. If we want the device to be more efficient at methylmercury conversion, efforts should be directed towards
improving the enzymatic activity of MerA and MerB.
Policies & Practices
Our Policy and Practices approach this year has focused on establishing an effective two-way discourse between our team and the public in order to inform our design, educate the public, and illuminate ethical issues related to both our project and integration of public opinion into project implementation. We focused our discussion on safety, ethics, and sustainability in order to design a project that fits the needs of the public while maintaining technical viability. Our team did extensive educational outreach in addition to educating ourselves on public perception of our work. We used this input to inform our device design such that it could be implemented in a way that addresses the major concerns of both scientists and consumers. We also took steps to protect our intellectual property and to educate ourselves about the patent process. Finally, our team sought to investigate ethical issues brought up by our discourse with the public by discussing both our work and ethics related to the project with a variety of experts and ethicists.
Educational Outreach
Building on past successes, our team has been devoted to volunteering our services to the community in a number of educational venues. The team took our curriculum, first developed in 2013, and improved the structure and delivery of our lesson plans in the hopes of encouraging awareness and education on topics in synthetic biology. Since 2013 our educational outreach group ECORI (Educating Communities On Research Innovation) has taught our [[File:original, interactive classroom curriculum]] to over 200 students (K-12) and their teachers. This year we also created a mobile exhibit form of our curriculum along with a layman’s introduction to our project that we displayed on over half a dozen weekends to visitors of all ages at the Science Museum of Minnesota. Our curriculum has also been brought to several other STEM fairs and family fun events in the Twin Cities area including the 3M Science Day Fair for 3M employees and their families, UMN Biodiversity Fair, CSE Family Fun Fair, and the Middle School STEM Fair hosted by the Association of Multicultural Students at UMN. Finally, the team designed a Synthetic Biology Game Show that was presented on stage with 30 participants at the Minnesota State Fair to assess the general public’s knowledge of the subject and teach hundreds of passers-by in a way that was both engaging and interactive. Winners were rewarded with reusable bags, magnets, and gift cards donated by our sponsors. In the spirit of science, our curriculum has been ever evolving to constantly address salient topics and educational materials. The variable versions of our curriculum allow it to be flexible and practical in various settings.
Public Perception
Our team sought to inform the majority stakeholders in our community concerning the scope of our project. This year our team chose to have an exhibit catered towards adult residents at the Minnesota State Fair (the largest statewide annual gathering with over 1.8 million visitors each year) to learn how we can best design our technology to meet the needs and concerns of the people whose waters we hope to bioremediate. We delivered a short synopsis of our device, the synthetic biology involved, and safety precautions we have outlined for our project. We then presented visitors with a five question survey using a Likert Scale to gauge public perception of both our device, and the synthetic biology methods used. The survey was a huge success with over 320 participants. With such a diverse attendance, our survey captured a great cross-section of the Minnesota community that would be impacted by the implementation of our device. The results of our survey, illustrated below, informed how and where the public would be most comfortable with implementing our device, and illustrated the need for catered education addressing the public’s major concerns prior to applying our device in the environment. Our model for gauging public perception allowed for a wide, diverse crowd to be accessed. This model can be used upon request.
Intellectual Property
Documentary
We compiled this documentary in order to inform those unfamiliar with the problem of global mercury contamination and to discuss the bioethical questions of synthetic biology as they related to our device implementation. We have conducted interviews with specialists from environmental toxicology, biotechnology, and philosophy at the University of Minnesota. Through our collaboration with the 2014 Colombia iGEM Team, we further examined the current methylmercury contamination in Colombia and around the globe.
Safety in the Lab
Our Training
DEHS Introduction: Research Safety
DEHS Chemical Safety
DEHS Waste Management
Safety in the Lab
2. Our Local Rules and Regulations Who is responsible for biological safety at our institution? The project was discussed with the Department of Environmental Health and Safety at our university, and a plan was devised for mercury waste disposal based on their input. General biosafety guidelines found at https://www.dehs.umn.edu/bio.htm, http://www.dehs.umn.edu/bio_pracprin.htm and http://www.cdc.gov/biosafety/publications/bmbl5/bmbl.pdf were followed.
Safety in the Lab
3. Risks of Your Project Now To mitigate risks to the safety and health of team members, or other people working in the lab: Gloves are used in any protocol that utilizes Ethidium Bromide, including gel electrophoresis. Lab coat, gloves, and full face shields are used when cutting gel fragments in proximity of ultraviolet light. For handling mercury, a lab coat, inner and outer (long cuffed) nitrile gloves, lab goggles and face shields will be used, and used materials will be disposed of by the University of Minnesota Department of Environmental Health and Safety. There are assigned incubators, hoods, and disposal containers for hazardous materials like mercury chloride. Design features to minimize risk kill switch proposal that would not allow the bacteria to survive outside of the encapsulation or even device holding the cells Air tight? non pathogenic lab strains
Attributions
Sponsors
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